TW472125B - Sodium-based dechlorinating agent, flue gas dechlorinating method using the same and waste treatment equipment - Google Patents
Sodium-based dechlorinating agent, flue gas dechlorinating method using the same and waste treatment equipment Download PDFInfo
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- TW472125B TW472125B TW089123130A TW89123130A TW472125B TW 472125 B TW472125 B TW 472125B TW 089123130 A TW089123130 A TW 089123130A TW 89123130 A TW89123130 A TW 89123130A TW 472125 B TW472125 B TW 472125B
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- F—MECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
- F23—COMBUSTION APPARATUS; COMBUSTION PROCESSES
- F23J—REMOVAL OR TREATMENT OF COMBUSTION PRODUCTS OR COMBUSTION RESIDUES; FLUES
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- B01D53/34—Chemical or biological purification of waste gases
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- B01D53/685—Halogens or halogen compounds by treating the gases with solids
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- F23—COMBUSTION APPARATUS; COMBUSTION PROCESSES
- F23J—REMOVAL OR TREATMENT OF COMBUSTION PRODUCTS OR COMBUSTION RESIDUES; FLUES
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- B01D2257/00—Components to be removed
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- B01D2257/204—Inorganic halogen compounds
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- F—MECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
- F23—COMBUSTION APPARATUS; COMBUSTION PROCESSES
- F23G—CREMATION FURNACES; CONSUMING WASTE PRODUCTS BY COMBUSTION
- F23G2201/00—Pretreatment
- F23G2201/30—Pyrolysing
- F23G2201/304—Burning pyrosolids
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- F—MECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
- F23—COMBUSTION APPARATUS; COMBUSTION PROCESSES
- F23G—CREMATION FURNACES; CONSUMING WASTE PRODUCTS BY COMBUSTION
- F23G2202/00—Combustion
- F23G2202/10—Combustion in two or more stages
- F23G2202/104—Combustion in two or more stages with ash melting stage
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- F—MECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
- F23—COMBUSTION APPARATUS; COMBUSTION PROCESSES
- F23J—REMOVAL OR TREATMENT OF COMBUSTION PRODUCTS OR COMBUSTION RESIDUES; FLUES
- F23J2215/00—Preventing emissions
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- F—MECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
- F23—COMBUSTION APPARATUS; COMBUSTION PROCESSES
- F23J—REMOVAL OR TREATMENT OF COMBUSTION PRODUCTS OR COMBUSTION RESIDUES; FLUES
- F23J2215/00—Preventing emissions
- F23J2215/30—Halogen; Compounds thereof
- F23J2215/301—Dioxins; Furans
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- F—MECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
- F23—COMBUSTION APPARATUS; COMBUSTION PROCESSES
- F23J—REMOVAL OR TREATMENT OF COMBUSTION PRODUCTS OR COMBUSTION RESIDUES; FLUES
- F23J2215/00—Preventing emissions
- F23J2215/60—Heavy metals; Compounds thereof
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Abstract
Description
472125 A7 B7 五.、發明説明(.1 ) 發明背景: 1 .發明領域: (讀先閲讀背面之注意事項再填寫本頁) 本發明係關於一種鈉系脫氯劑、一種使用該脫氯劑之 煙道氣脫氯方法及一種廢棄物處理設備。 2 ·相關技藝之敘述: 一種對含有氯化氫煙道氣的處理裝置,例如設在將廢 棄物送到焚化處理的廢棄物處理設備中。在此廢棄物處理 設備中’順序配置第一集塵器及第二集塵器,在以/第一集 塵器去除如煙道氣中所含燃燒飛灰的灰塵之後,再於第二 集塵器中進行煙道氣的脫氯。 爲了在第二集塵器中進行脫氯,煙道氣進入第二集塵 器之前先加入脫氯劑。過去常主要使用如氫氧化鈣( 經濟部智慧財產局8工消費合作社印製 C a ( Ο Η ) 2 )的鈣系脫氯劑做爲脫氯劑,氫氧化鈣若加 入煙道氣中,會與煙道氣中的氯化氫(H C 1 )反應,產 生的脫氯殘留物含有氯化鈣(C a C 1 2 )、氧化鈣 C a 0 )及其類似者。然而,所產生的脫氯殘留物的用途 只在於以氯化鈣作爲雪溶劑或濕氣吸收劑的狹隘有效利用 範圍。脫氯殘留物大多以化學處理或水泥將其固化 > 並以 回收處置,然而回收場址的取得已越來越困難。 因此建議使用鈉系脫氯劑如碳酸氫鈉(重碳酸鈉.: N a Ή C 0 3 ).或碳酸鈉(蘇打灰:N a 2 C ◦ 3 ) ’取代 鈣系脫氯劑。如此,當鈉系脫氯劑加入煙道氣中時:’煙道 氣中所含的氯化氫會成爲氯化鈉(N a C 1 ) ’將水加入 脫氯殘留物中可溶解氯化鈉。所以,溶在水中的水溶性組 本紙張尺度適用中國國家標準(CNS ) A4規格(210X297公釐) -4 - 472125 經濟部智慧財產局員工消費合作社印製 A7 B7 五、發明說明(2 ) 成可稀釋並排放,而分離出無法溶於水中的非水溶性組成 ’並送至熔融爐中進行燃燒處理,.因此可減少棄置至回收 再用的需要性。 當以碳酸氫鈉作爲鈉系脫氯劑且碳酸氫鈉的粒徑大於 3 0 // m時,粉末顆粒間不會膠結,且此藥劑在粉末狀態 很穩定。然而,粒徑大於3 0 // m的碳酸氫鈉會導致很低 的氯化氫去除比率,因此以其作爲脫氯劑並不恰當。所以 ’通常以碳酸氫鈉作爲鈉系脫氯劑時,會將其硏磨成粒徑 爲3 Ο μ m或更小。 然而,將碳酸氫鈉硏磨成粒徑爲3 0 # m或更小時, 粉末顆粒會膠結使形狀成爲纖維狀灰塵球或像石頭的塊狀 物,硏磨後的碳酸氫鈉無法以粉末狀態穩定存在,使得不 可能穩定地將其供應至煙道氣。 爲解決此缺點,常用的方法爲使用防結塊劑。在習知 的技藝中,已利用疏水性的防結塊劑作爲防結塊劑,疏水 性防結塊劑會帶來明顯的固化抑制效應。添加疏水性防結 塊劑的碳酸氫鈉具有高可流動性及可氾流性的特性,且在 粉末狀態可展現令人滿意的穩定性。 然而,添加疏水性防結塊劑的碳酸氫鈉加到煙道氣中 作爲脫氯劑時,與碳酸氫鈉鍛燒後的氯化氫反應產生的顆 粒(亦即中和的殘留物)及防結塊.劑的顆粒,二者皆具有 高可流動性,容易卡在附在第二集塵器中的濾布內,此集 塵器含有例如袋式集塵器。當中和的殘留物顆粒或防結塊 劑的顆粒穿透進入濾布中時,會產生結塊,在濾布導致過 本紙張尺度適用中國國家標準(CNS)A4規格(210 X 297公釐) (請先閱讀背面之注意事項再填寫本頁) 裝 —1— 訂·! I!--«^, -5- 472125 A7 五、發明說明(3 多的壓降而不可能繼續操作。即使是使 式集塵器進行反沖洗,仍難以淸除結塊。 更進一步的是,與碳酸氫鈉鍛燒後 的部分顆粒(亦即中和的殘留物)會卡 塊劑的顆粒穿過濾布,導致脫氯劑及中 雙織玻璃布常用來作爲濾布,爲避免脫 的洩漏’需要使用表面上塗佈鐵弗龍薄 製的特殊濾布。然而,使用時若此薄膜 臨化學品從此部位拽漏的新問題。 本發明的目的爲避免發生過高的壓 的濾布洩漏。 發明節要: 爲了解決上述問題的目的,本發明對鈉系脫氯劑做了 改善。較特別的是,本發明的鈉系脫氯劑含有碳酸氫鈉與 親水性防結塊劑的混合物,所具有的靜止角度爲4 0 °或 更高、分散性小於5 0及可氾流性指數小於9'0。 經濟部智慧財產局員工消費合作社印製 用脈波的空氣對袋 的氯化氫反應產生 在濾布中,且防結 和的殘留物洩漏。 氯劑及中和殘留物 膜的雙織玻璃布所 受損或剝落,會面 降或附在集塵器上 (請先閱讀背面之注意事項再填寫本頁) 依據具有上述特性的鈉系脫氯劑,其中親水性防結塊 劑具有輕微的黏著性,碳酸氫鈉與防結塊劑顆粒的可流動 性變得較爲遲緩:碳酸氫鈉或防結塊劑顆粒不會進到濾布 內,而在濾布的表面上形成一個穩定的過濾層。結果便可 能預防濾布內產生過高壓降或發生濾布的洩漏。 利用Hosokawa Micron公司所製的P T - D型粉末測試 機,測量物理特性。 本紙張尺度適用中國國家標準(CNS)A4規格(210 X 297公釐) -6- 472125 A7 B7 五、發明說明(4 ) (請先閱讀背面之注意事項再填寫本頁) 靜止角度的測量進行方式爲在篩網震動下使粉末狀樣 品通過直徑爲8 Omm、網子開口爲7 1 0 /zm的篩網, 緩慢讓過篩的樣品從高度爲1 6 0 m m的漏斗掉落到直徑 爲8 0 m m的水平桌上’當粉末所形成圓錐體的產生線與 水平面之間產生角度時,根據可流動性較高取較小値。測 量粉末的掉落量,直到靜止角度大體上已穩定爲止。 可氾流性指數値是以數字化評估氾流特性的判斷標準 。藉由決定從表5及6所測量的可流動性指數値、掉落角 度、差異角度及可分散性,可氾流性指數値定義爲可將谭 些指數加總的値:較大的値相當於較高的可氾流性特性。 現在說明個別的物理特性定義,可.流動性指數値係以類似 方式決定的指數所決定’來自於靜止角度、可壓縮性、抹 刀角度及一致性係數的測量値,並以這些指數値的加總値 表示。靜止角度係以上述方法決定的。 可壓縮性定義爲: (塡充的總體密度-通氣的總體密度)/塡充的總體密度X 1 ◦ ◦ 經濟部智慧財產局員工消費合作社印製 通氣的總體密度的決定方式爲在篩網震動下使粉末狀 樣品通過直徑爲8 Omm、網子開口爲7 1 0 的篩網 ,並讓在篩網下方的粉末裝塡在內體積爲1 〇 〇 c m3的容 器中’作爲測量的粉末質量。塡充的總體密度的決定方式 爲輕拍含有粉末的容器,在1 8 0秒的時程內一次一次的 拍1 8 0下’並測量相當於體積爲χ 〇 〇 c m 3的質量。抹 本紙張尺度適用中國國家標準(CNS)A4規格(210 X 297公髮) 472125 經濟部智慧財產局員工消費合作社印製 A7 B7 五、發明說明(5 ) 刀角度的決定方式爲讓以金屬所製的、尺寸爲1 2 〇 X2 2 m m的抹刀保持水平,並測量累積在其上的粉末側表面的 傾斜角度。 一致性的定義爲在以篩分析所測得的粒徑分佈而得累 積的質量分佈中,以累積較小尺寸(undersize )分佈中 6 0 %處的粒徑除以累積較小尺寸分佈中1 〇 %處的粒徑 的値。粒徑分佈可用不同的方法決定,如篩分析及雷射繞 射散射方法,其可反映出待測量粉末的粒徑及類似者。本 發明採用雷射繞射散射方法所測量的値’係利用Nikkiso有 限公司所製的「Microtrack F R A 9 2 2 0」測量。 掉落角度的決定方式爲以附在測量儀器上的振動器, 對以測量靜止角度爲目的所形成的粉末圓錐體施以固定的 衝擊力三次,並測量因掉落後所形成的圓錐體傾斜角度。 差異角度的決定方式爲以靜止角度的値扣除掉落角度 的値而得。 可分散性的決定方式爲將1 0 g粉末樣品一次從6 1 • ·....... ... c m高丟在直徑1 〇 c m、凹面朝下的錶玻璃上,粉末樣 品散落在錶玻璃外的質量與相對於所丟下的粉末樣品總質 量的百分比。高於此値的粉末樣品通常具有高分散性與可 氾流性。 碳酸氫鈉較佳應該爲平均粒徑在自2 // m至3 0 // m 的範圍內。平均粒徑大於3 0 # m時,鈉系脫氯劑與氯化 氫之間的反應會變得不足;另一方面,平均粒徑小於2 # m時’需要花很多時間及勞力硏磨。爲了使鈉系脫氯劑 本紙張尺度適用中國國家標準(CNS)A4規格(210 X 297公釐) —Μ--------訂--------線 (請先閱讀背面之注意事項再填寫本頁) -8- 472125 A7 B7 五、發明說明(6 ) 達到足夠的反應,平均粒徑在2 # m至3 0 # m範圍內已 能滿足需求,平均粒徑在2 // m至1 0 # m範圍內則能有 (請先閱讀背面之注意事項再填寫本頁) 較高的反應,所以較爲推薦。 可利用的防結塊劑通常包括矽膠、硬脂酸鎂、硬脂酸 鈣及碳酸鎂。 本發明中的親水性抗結塊劑較佳應該含有矽膠,且較 佳應該以0 . 1 %或更多的量混在脫氯劑的總質量中。少 於0 · 1 %的量並不足以獲得抗結塊效應。因爲親水性抗 結塊劑不溶於水中,藥劑的高度扮合比率需要相當多的時 間與勞力,以處理脫氯的殘留物,所以,親水性抗結塊劑 更佳應以0 . 1 %至5 %範圍內的量混在脫氯劑的總質量 中〇 更進一步的是,親水性抗結塊劑的平均粒徑較佳應該 在0 . 0 0 1 # m至1 # m範圍內。較小的平均粒徑會有 更突出的抗結塊效應,但在技術上並不容易以低成本 '工 業化的方式讓粉末的粒徑小於0 . 0 0 1 # m ;平均粒徑 大於1 m會有較小的抗結塊效應。所以較佳應該在 ◦ . 0 ◦ 1 # m至1 // m範圍內。 經濟部智慧財產局員工消費合作社印製 本發明中的廢棄物處理設備包括熱裂解反應器,其使 廢棄物熱裂解,產生熱裂解氣體及主要含有非揮發性組成 的熱裂解殘留物;分離機構將熱裂解殘留物分成可燃性組 成及非可燃性組成;燃燒熔融爐可讓熱裂解氣體與可燃性 組成導入使其燃燒,並排放熔融爐石及煙道氣;第一煙道 氣處理機構去除煙道氣中的灰塵;第二煙道氣處理機構在 本紙張尺度適用中國國家標準(CNS)A4規格(210 X 297公釐) -9 - Α7 Β7 五、發明說明(7 ) 自第一煙道氣處理機構排出的煙道氣中,加入脫氯劑進行 脫氯;分離器藉由將水加到由第二煙道氣處理機構所產生 的脫氯殘留物中,從含有溶在其中的脫氯殘留物的水溶液 中’分離出不溶於水的非水溶性組成;p Η改性劑調整由 分離器分離出非水溶性組成後剩下的水溶液的ρ Η ;及至 少另一個戴奧辛去除單元,以去除來自於第二煙道氣處理 機構產生的脫氯殘留物及/或來自於其ρ Η已經過ρ Η改 性劑調整過的水溶液中的戴奧辛與類似者;其中鈉系脫氯 劑係加在第二煙道氣處理機構中。 如上所述,去除來自於ρ Η已經過ρ Η改性劑調整過 的水溶液的戴奧辛及類似者的戴奧辛去除單元,可設置作 爲戴奧辛去除單元。設置可去除第二煙道氣處理機構產生 的脫氯殘留物中的戴奥辛與類似者的戴奧辛去除單元,可 取代這個對已調整過ρ Η的水溶液去除戴奧辛的戴奧辛去 除單元。當設有可去除第二煙道氣處理機構產生的脫氯殘 留物中的戴奧辛與類似者的戴奧辛去除單元時,此戴奧辛 去除單元可幾乎完全地去除戴奧辛與類似者,但爲了去除 未被去除的戴奧辛與類似者,第二戴奧辛去除單元可設在 Ρ Η改性劑的下游。 藉由使用螯合樹脂或螯合劑(以下總稱爲「螯合物質 J ),可能可去除在分離非水溶性組成後留在水溶液中的 ΤΤΤ. 水 ° 更進一步的是,可在上述廢棄物處理設備中的第二煙 道氣處理機構的上游設置混合碳酸氫鈉與親水性防結塊劑 本紙張尺度適用中國國家標準(CNS)A4規格(210 X 297公釐) (請先閱讀背面之注意事項再填寫本頁) 裝— II訂-------I 線 經濟部智慧財產局員工消費合作杜印製 -10- 經濟部智慧財產局員工消費合作社印製 472125 Α7 _____ Β7 五、發明說明(8 ) 的混合器,及硏磨碳酸氫鈉的硏磨機。可在上述廢棄物處 理設備中的p Η改性劑的下游,增加可去除p Η已被p Η 改性劑所調整的水溶液中的汞。 本發明中的煙道氣脫氯方法所含的步驟爲將上述鈉系 脫氯劑加到煙道氣中,使煙道氣中所含的氯化氫與鈉系脫 氯劑反應而去除之。 更進一步的是,本發明中的煙道氣脫氯方法含有以下 步驟:使煙道氣中所含的氯化氫與鈉系脫氯劑反應,以脫 氯殘留物去除之;從脫氯殘留物中去除戴奧辛及類似者; 然後加水溶解脫氯殘留物,從溶解脫氯殘留物的水溶液中 分離出無法溶解於水中的非水溶性組成;及對分離出非水 溶性組成後剩下的水溶液調整Ρ Η。 在上述煙道氣脫氯方法中,無法完全去除的戴奧辛及 類似者可在ρ Η調整後再度被去除。 圖形之簡要敘述: 圖1爲系統示意圖,說明以本發明的鈉系脫氯劑方法 ,可進行脫氯裝置的實例。 圖2爲系統示意圖’說明以本發明的鈉系脫氯劑方法 ,可進行脫氯裝置的另一實例。 圖3爲系統示意圖,仍說明以本發明的鈉系脫氯劑方 法,可進行脫氯裝置的另一實例。 圖4爲系統示意圖’說明以本發明的鈉系脫氯劑方法 ,可進行脫氯裝置更進一步的另一實例。 本紙張尺度適用中國國家標準(CNS)A4規格(210 X 297公釐) I^--------訂---------線- (請先閱讀背面之注意事項再填寫本頁) -11 - 472125 A7 B7 五、發明說明(9 ) 圖5爲系統不意圖’說明以本發明的鈉系脫氯劑方法 ,可進行脫氯裝置的另一實例。 圖6爲系統示意圖’說明一種廢棄物處理設備作爲本 發明更進一步的另一實例。 主要元件對照表 2 熱裂解反應器 4 分離器 5 硏磨機 6 燃燒熔融爐 8 熱交換器 10 廢熱鍋爐 12 降溫塔 14 第一集塵器 16 第二集塵器 18 硏磨機 2 0 煙道 2 2 溶解槽 2 4 繼電器槽 2 6 分離器 2 8 p Η調整槽 32 戴奧辛去除單元 32a 戴奧辛去除單元 3 4 廢水槽 (請先閱讀背面之注意事項再填寫本頁) 裝!!_ —訂---------線 經濟部智慧財產局員工消費合作社印製 本紙張尺度適用中國國家標準(CNS)A4規格(210 X 297公釐) -12- 472125 A7 B7 五、發明說明(ίο) 經濟部智慧財產局員工消費合作社印製 3 5 混合器 a 廢棄物 b 熱裂解殘留物 c 熱裂解碳 d 1 有價値物品 d 2 殘渣 e 熔融爐石 f 1 粉塵 f 2 粉塵 f 3 粉塵 g 脫氯齊if g 1 碳酸氫鈉 g 2 親水性防結塊劑 A 熱空氣 G 1 熱裂解氣 G 2 燃燒煙道氣 G 3 煙道氣 G 4 煙道氣 G 5 煙道氣 G 6 煙道氣 G 7 煙道氣 h 脫氯殘留物 i 水 j 水溶液 (請先閱讀背面之注意事項再填寫本頁) 裝--------訂---------線 本紙張尺度適用中國國家標準(CNS)A4規格(210 X 297公釐) -13- 472125 經濟部智慧財產局員工消費合作社印製 A7 B7 五、發明說明(11 ) k 非水溶性組成 w 水 較佳具體實例之詳細敘述: 參考圖形說明本發明的具體實例。 圖1爲以本發明所用的鈉系脫氯劑方法,可進行脫氯 裝置的系統示意圖。本實例代表本發明對如處理煙道上產 生的煙道氣G 5的煙道氣脫氯的應用。如圖1所示,煙道 热脫氯裝置包含作爲第一煙道氣處理機構的第一集塵器 1 4 ’及作爲第二煙道氣處理機構的第二集塵器1 6 ,以 進行二階段的灰塵收集。 煙道氣G 5係在處理的廢棄物送到第一集塵器1 4時 産& ’第一集塵器1 4去除來自於煙道氣G 5的灰塵(焚 化飛灰)ί 1 ’已去除灰塵f 1的煙道氣G 6再送到第二 集麈器1 6 ’此時,在第二集塵器1 6上游中的流動通道 中加人本發明的鈉系脫氯劑g。因爲灰塵f丨已預先在第 一集塵器1 4中被去除,第二集塵器1 6中的脫氯殘留物 h幾乎已沒有灰塵f 1 ,結果,與單一集塵器的情況相比 ’此脫氯殘留物h更容易處置。. 鈉系脫氯劑g含有碳酸氫鈉(重碳酸鈉:N a H C 0 3 )與親水性防結塊劑的混合物。碳酸氫鈉應該硏磨至平均 粒徑在2 // m至3 〇 # m範圍內,或較佳爲在2 # m至 1 0 // m ’並以〇 . 1質量%或更多的量與矽膠系親水性 防結塊劑混合,或較佳以在〇 . 1質量%至5質量%範圍 本紙張尺度適用中國國豕標準(CNS)_A4規格(210 X 297公髮) (請先閱讀背面之注意事項再填寫本頁) 裝·! 訂---— —— — —線 -14- 472125 經濟部智慧財產局員工消費合作杜印製 A7 B7 五、發明說明(12) 內。親水性防結塊劑的平均粒徑應該在Q . 0 0 1 // m至 1/zm範圍內,或較佳在0 · 00 1//m至〇 . l#m範 圍內。可利用的親水性防結塊劑包括例如由Tokuyama公司 所製造的蒸燻(fumed )親水性矽膠。當碳酸氫鈉顆粒硏磨 至粒徑在2 # m至3 0 # m範圍內時,反應由顆粒表面到 達內部,且細小粒徑確保對濾布能良好的附著及令人滿意 的利用效率。當煙道氣含有硫氧化物時,鈉系脫氯劑g可 作爲脫硫劑,使其可能在脫氯的同時於第二集塵器1 6中 完成脫硫。 當加入鈉系脫氯劑g時,與煙道氣所含的氯化氫( HC 1 )反應產生的氯化鈉(Na C 1 )便自第二集塵器 1 6以脫氯殘留物排放。脫氯煙道氣G 7以淨化的氣體由 煙道2 0排放。 另一方面,由第二集塵器1 6所去除的脫氯殘留物h 加水i並在溶解槽2 2中溶解,更進一步送到繼電器槽 2 4,並以水溶液j貯存。當加水i時,脫氯殘留物h中 的水溶性組成溶解在水中,但是非水溶性組成k不溶於水 中,而在水溶液中成爲懸浮性物質。 然後,產生的水溶液j送到分離器2 6 ,以例如過濾 將其分離,及將形成懸浮物的非水溶性組成k自水溶液中 分離。分離後的非水溶性組成k回到如後所述的熱裂解反 應器(未示出),最後在燃燒溶融.爐內將其轉化成熔融爐 石後’排放至系統外。此時,非水溶性組成k中的戴奧辛 及類似者可在燃燒熔融爐中分解而完全去除。 本紙張尺度適用中國國家標準(CNS)A4規格(210 X 297公釐) 』 -15 - --------^---------^ (請先閲讀背面之注意事項再填寫本頁) 472125 經濟部智慧財產局員工消費合作社印製 A7 B7 五、發明說明(13) 將非水溶性組成k分離後剩下的水溶液1含有水溶性 組成’送到下一個調整P Η的ρ Η調整槽2 8的程序中。 加入如氯化氫(H C 1 )酸性物質的ρ η調整劑,使中和 溶在水中未反應的脫氯劑。更進一步的是,送到戴奧辛去 除單元的戴奧辛及類似者可被去除。爲了去除戴奧辛及類 似者’係讓水溶液通過活性碳塡充床或類似者,使用去除 戴奧羊及類似者的活性碳吸附方法。自上述剩下的水溶液 1中去除戴奧辛後而得的水溶液1以處理水w貯存在廢水 槽3 4中。上述水溶性組成中,惟有內含如氯化鈉溶解性 鈉鹽的水溶液經ρ Η調整後,方排放至海洋、河川及污水 處置場。就戴奧辛的些微含量而言,在分離非水溶性組成 後’才去除水溶液1中的戴奧辛及類似者,此方式比熱裂 解的設備更簡單且成本更低。 如圖1所示,爲了去除從分離器2 6出來剩下的水溶 液1中所含的戴奧辛及類似者,在ρ Η調整槽2 8下游設 置戴奧辛去除單元3 2,也可能可預先去除在脫氯殘留物 h中的戴奧半及類似者。較特別的是,如圖2所示,戴奧 辛去除單元3 2 a配置在第二集塵器1 6及溶解槽2 2之 間,使得從第二集塵器1 6出來的脫氯殘留物h在溶解於 水中之前’去除脫氯殘留物h中所含的戴奧辛及類似者。 可使用的戴奧辛去除單元3 2 a包括如加熱脫氯單元。 如上所述的特性’戴奧辛及類似者幾乎可完全地從戴 奧辛去除單元3 2 a所排放的脫氯殘留物中去除。所以, 不只是非水溶性組成k中,在剩下的水溶液1中也幾乎未 本紙張尺度適用中國國家標準(CNS)A4規格(210 X 297公髮) (請先閱讀背面之注意事項再填寫本頁) "--------訂---------線| -16- 472125 A7 B7 五、發明說明(14) 含有戴奧辛或類似者。 (請先閱讀背面之注意事項再填寫本頁) 更進一步的是,也可採用如圖3所示的特性,其中戴 奧辛去除單元3 2係配置在P Η調整槽2 8的下游,且戴 奧辛去除單元3 2 a配置在第二集塵器1 6及溶解槽2 2 之間。亦即,戴奧辛及類似者幾乎可以完全地被戴奧辛去 除單元3 2 a所去除。若產生戴奧辛及類似者在去除後仍 然殘留的問題時,在P Η調整後,戴奧辛去除單元3 2仍 能完全去除戴奧辛及類似者。 經濟部智慧財產局員工消費合作社印製 也可採用如圖4所示的特性,其中混合器3 5及硏磨 機1 8的設置機構爲硏磨碳酸氫鈉與混合親水性防結塊劑 。通常,因爲碳酸氫鈉g 1所具有的平均粒徑在5 0 /zm 至2 7 0 // m範圍內,程序中所含的步驟包括:以對碳酸 氫鈉g 1爲0 . 1質量%的量,添加平均粒徑在 ◦ . 0 0 1 // m至1 Μ IB範圍內的親水性矽膠,作爲親水 性防結塊劑g 2 ;在混合器3 5中混合碳酸氫鈉g 1與親 水性防結塊劑g 2 ;在硏磨機1 8中硏磨所產生的混合物 ,使平均粒徑在2 μ m至3 0 // m範圍內,而產生鈉系脫 氯劑g。將此鈉系脫氯劑g加到煙道氣G 6中,其中的粉 麈f 1已被第一集塵器1 4所去除。因爲硏磨至平均粒徑 在2 # m至3 0 # m範圍內的碳酸氫鈉粒徑很小,會由顆 粒表面反應至內部,且對袋式集塵器的濾布有良好的附著 性質。因此可確保令人滿意的利用效率。 如圖4所示的特性,其中戴奧·辛去除單元3 2係配置 在pH調整槽2 8的下游,而戴奧辛去除單元3 2 a也可 本紙張尺度適用中國國家標準(CNS)A4規格(210 X 297公釐) -17- 472125 經濟部智慧財產局員工消費合作社印製 A7 B7 五、發明說明(15) 如圖2所示的特性,配置在第二集塵器1 6及溶解槽2 2 之間。更進一步的是,如圖3所示的特性,戴奧辛去除單 元3 2可配置在P Η調整槽2 8的下游,且戴奧辛去除單 元3 2可配置在第二集塵器1 6及溶解槽2 2之間。 如圖5所示,也可能在PH調整槽2 8及戴奧辛去除 單元3 2之間配置汞去除單元3 0,目的在於去除從分離 器2 6出來剩下的水 '丨谷液1中所含的亲。 利用此特性,於分離器2 6分離出非水溶性組成k之 後所剩下的水溶液1的p Η於p Η調整槽2 8中調整後, 屬於一種重金屬的汞可被汞去除單元3 0所去除。汞可用 例如沈澱法、離子交換法或吸附方法而去除。在沈澱法中 ,可行的技術包括使產生硫化汞型態的沈澱,或使用具有 二硫氨基甲酸酯及類似者的重金屬捕捉劑。在離子交換法 中,當汞以例如鹵化錯合離子的陰離子存在時,使用陰離 子交換樹脂。在吸附方法中,利用螯合效應對特定重金屬 具有高選擇性的螯合樹脂、活性碳或活性焦炭。可用的螯 合樹脂包括例如以聚丙烯、聚苯乙烯或酚樹脂作爲基質, 以硫醇、二硫氨基甲酸酯、isothuronium、二苯基硫腙、硫 脲或多胺等類型作爲配位自由基。可用的活性碳種類包栝 例如氣體活化的活性碳、氯化鋅活化的活性碳、粒狀活性 碳、椰殼活性碳及粒狀活性碳黑。在這些方法中,使用螯 合物質如螯合劑或螯合樹脂的方法較佳,因爲簡單又準確 〇 將已經去除汞的水溶液導入戴奧辛去除單元3 2,以 本紙張尺度適用中國國家標準(CNS)A4規格(210 X 297公釐) (請先閱讀背面之注意事項再填寫本頁) I 裝!| 訂--I--!1·線· -18- 472125 經濟部智慧財產局員工消費合作社印製 A7 B7 五、發明說明(16) 去除戴奧辛及類似者。適用的戴奧辛去除方法與前述在圖 1所示情況者相同。 圖5中’戴奧辛去除單元3 2配置在位於汞去除單元 3 0下游的p Η調整槽2 8的下游。然而,如圖2所示, 戴奧辛去除單元3 2 a也可配置在第二集塵器1 6及溶解 槽2 2之間。更進一步的是,如圖3所示,戴奧辛去除單 元3 2配置在p Η調整槽2 8的下游,且戴奧辛去除單元 3 2 a可配置在第二集塵器1 6及溶解槽2 2之間。 現在將參考圖6說明處理廢棄物與所產生的煙道氣的 廢棄物處理設備。圖6爲系統示意圖,說明本發明一種廢 棄物處理設備的實例。 如圖6所示,在此廢棄物處理設備中,如市鎭廢棄物 的廢棄物a硏磨至1 5 0 m m 2以下,再以如螺旋進料機的 導入機構導入熱裂解反應器2中。舉例而言,以水平式旋 轉鼓作爲熱裂解反應器2,熱裂解反應器2的內部以密封 機構(未示出)維持在低氧的環境下,由配置在燃燒熔融 爐6下游的熱交換器8所加熱的下游中的熱空氣A從線 L 1導入。 導至熱裂解反應器2中的廢棄物a以熱空氣A加熱至 溫度在3 0 ◦至6 0 0 °C範圍內,或通常約在4 5 〇°C, 如此使廢棄物a的熱裂解產生熱裂解氣G 1及主要爲非揮 發性的熱裂解殘留物b。在熱裂解反應器2中所產生的熱 裂解氣G 1及熱裂解殘留物b以排放單元(未示出)將其 分離,熱裂解氣G 1經由線L 2輸送,此線爲熱裂解氣通 本紙張尺度適用中國國家標準(CNS)A4規格(210 X 297公釐) I!-----·"1--訂-------線 (請先閱讀背面之注意事項再填寫本頁) -19- 472125 經濟部智慧財產局員工消費合作社印製 A7 B7 五、發明說明(17) 到燃燒熔融爐6的燃燒器的管線。 依據本發明者所獲得的發現,隨著廢棄物a的種類而 改變的熱裂解殘留物b可發現含有如下的質量% : 可燃性成份大部份相對含有 細小的粒狀物: 1 〇至6 0 % 相對細小的灰燼: 5至4 0 % 粗的金屬粒狀物: 7至5 0 % 粗的殘渣、陶瓷、水泥等:1 〇至6 0 % 在相當高的約4 5 0 t溫度下排放的熱裂解殘留物b 以冷卻單兀(未在圖中示出)冷卻至約8 0 C ’並導入作 爲分離機構的分離器4中,在此殘留物被分成可燃性組成 的熱裂解碳c ,及非可燃性組成的有價値物品d 1與殘渣 d 2。振動篩網、磁分離器及鋁的分離器與已知類似的分 離器皆可作爲分離器4。 從非可燃性組成分離而隨後排放出來的熱裂解碳c及 殘渣d 2以滾動式、管磨式、棒磨式或球磨式硏磨機5硏 磨,再送到燃燒熔融爐6。根據廢棄物的種類與特性適當 選用硏磨機5。在硏磨機中,熱裂解碳c及殘渣d 2應較 佳爲硏磨至粒徑1 m m或更小,再經由線L 3送到燃燒熔 融爐6的燃燒器中。 另一方面,以風扇(未示出)輸送的燃燒空氣、熱裂 解氣G 1及熱裂解碳c以在約1 3 0 0 °C高溫範圍的溫度 下,在燃燒熔融爐中燃燒。經過此燃燒後,由熱裂解碳c 及殘渣d 2的相當細小的灰燼顆粒產生的燃燒灰燼便熔化 本紙張尺度適用中國國家標準(CNS)A4規格(210 X 297公釐) 1---------- Ί ! β---------^ I (請先閱讀背面之注意事項再填寫本頁) -20- 472125 A7 B7 五、發明說明(18) (請先閱讀背面之注杳?事項再填寫本頁) 而產生熔融爐石e。將爐石自燃燒熔融爐6的爐石底部出 口丟進水槽中(未示出),熔融爐石e轉變爲水成粒狀爐 石。以一種裝置(未示出)使水成粒狀爐石限制成指定的 形狀,或成爲可再利用的建築材料或鋪面材料的粒狀物。 在廢棄物處理設備的燃燒熔融爐6中所產生的燃燒煙 道氣G 2在熱交換器8中進行熱回收,而成爲煙道氣G 3 ,其導入可將熱回收的廢熱鍋爐1 0,煙道氣G 3便轉變 成煙道氣G 4。將煙道氣G 4送到降溫塔1 2以降低其溫 度。已在降溫塔1 2降溫後的煙道氣G 5送到第一集塵器 1 4。灰塵f 2、f 3及f 1分別在廢熱鍋爐1 0、降溫 塔1 2及第一集塵器1 4中收集,伴隨著在分離器4分離 的熱裂解碳c ,氣體再經由線L 3及L 4回到燃燒熔融爐 6的燃燒器中,於燃燒熔融爐6中進行燃燒及熔化而變成 爐石。 經濟部智慧財產局員工消費合作社印製 由分離器2 6所分離的非水溶性組成k亦經由線L 5 回到熱裂解反應器2,最後再於燃燒熔融爐6中燃燒及熔 化而變成爐石。在此程序中,藉由形成爐石使重金屬變成 無害。送到第一集塵器1 4的煙道氣G 5隨後的處理與圖 5所示中的相同,故在此略過其說明。送到第一集塵器 1 4的煙道氣G 5隨後的處理可利用如圖1 、2或3所示 特性的處理系統完成。 實例 以本發明的鈉系脫氯劑進行實際應用的實驗。親水性 本紙張尺度適用中國國家標準(CNS)A4規格(210 X 297公釐) -21 - 472125 A7472125 A7 B7 V. Description of the invention (.1) Background of the invention: 1. Field of invention: (Read the precautions on the back before filling out this page) The present invention relates to a sodium-based dechlorinating agent and a dechlorinating agent using the same Flue gas dechlorination method and a waste treatment equipment. 2 · Description of related technologies: A treatment device for a flue gas containing hydrogen chloride, for example, a waste treatment device for sending waste to incineration. In this waste treatment equipment, the first dust collector and the second dust collector are arranged in sequence. After the first dust collector removes dust such as fly ash contained in the flue gas, the second dust collector Dechlorination of flue gas in a dust collector. For dechlorination in the second dust collector, a dechlorinating agent is added before the flue gas enters the second dust collector. In the past, calcium-based dechlorinating agents such as calcium hydroxide (C a (Ο 消费) 2 printed by the Industrial and Commercial Bureau of the Intellectual Property Bureau of the Ministry of Economic Affairs) were mainly used as dechlorinating agents. If calcium hydroxide is added to the flue gas, It will react with hydrogen chloride (HC 1) in the flue gas, and the dechlorination residue produced contains calcium chloride (C a C 1 2), calcium oxide C a 0) and the like. However, the use of the resulting dechlorinated residues lies only in the narrow and effective use of calcium chloride as a snow solvent or moisture absorbent. Most of the dechlorination residues are chemically treated or cement solidified > and disposed of by recycling, however, it has become increasingly difficult to obtain recycling sites. Therefore, it is recommended to use a sodium-based dechlorinating agent such as sodium bicarbonate (sodium bicarbonate: Na a Ή C 0 3). Or sodium carbonate (soda ash: Na 2 C ◦ 3) 'instead of a calcium-based dechlorinating agent. In this way, when the sodium-based dechlorinating agent is added to the flue gas: ‘the hydrogen chloride contained in the flue gas will become sodium chloride (N a C 1)’. Sodium chloride may be dissolved by adding water to the dechlorination residue. Therefore, the paper size of the water-soluble group dissolved in water applies the Chinese National Standard (CNS) A4 specification (210X297 mm) -4-472125 Printed by the Consumer Cooperative of the Intellectual Property Bureau of the Ministry of Economic Affairs A7 B7 V. Description of the invention (2) It can be diluted and discharged, and the insoluble components insoluble in water are separated and sent to a melting furnace for combustion treatment. Therefore, the need for disposal to recycling can be reduced. When sodium bicarbonate is used as a sodium-based dechlorinating agent and the particle size of the sodium bicarbonate is greater than 30 // m, the powder particles will not be cemented, and the agent is very stable in the powder state. However, sodium bicarbonate with a particle size larger than 30 / m leads to a very low removal rate of hydrogen chloride, so it is not appropriate to use it as a dechlorinating agent. Therefore, when sodium bicarbonate is usually used as a sodium-based dechlorinating agent, it is honed to a particle size of 30 μm or less. However, when honing sodium bicarbonate to a particle size of 30 # m or less, the powder particles will cement to form a fibrous dust ball or a block like a stone. The honed sodium bicarbonate cannot be used as a powder. Stability exists, making it impossible to stably supply it to the flue gas. To solve this disadvantage, a common method is to use an anti-caking agent. In the conventional art, a hydrophobic anti-caking agent has been used as an anti-caking agent, and the hydrophobic anti-caking agent brings a significant curing inhibiting effect. Sodium bicarbonate added with a hydrophobic anti-blocking agent has the characteristics of high flowability and flowability, and exhibits satisfactory stability in a powder state. However, when sodium bicarbonate added with a hydrophobic anti-caking agent is added to the flue gas as a dechlorinating agent, particles (that is, neutralized residues) and anti-caking generated by the reaction with sodium hydrogen carbonate after calcination. Both of the granules of the agent have high flowability and are easily stuck in a filter cloth attached to a second dust collector, which contains, for example, a bag type dust collector. When the neutralized residue particles or anti-caking agent particles penetrate into the filter cloth, agglomeration will occur. When the filter cloth causes the paper size to meet the Chinese National Standard (CNS) A4 specification (210 X 297 mm) (Please read the precautions on the back before filling out this page) Equipment—1— Order ·! I!-«^, -5- 472125 A7 V. Description of the invention (more than 3 pressure drops make it impossible to continue operation. Even if the dust collector is backwashed, it is still difficult to get rid of agglomerates. Furthermore, Some particles after calcination with sodium bicarbonate (that is, the neutralized residue) will block the particles of the blocking agent through the filter cloth, resulting in dechlorinating agents and double-woven glass cloth commonly used as filter cloth. Leakage 'requires the use of a special filter cloth made of Teflon thin on the surface. However, if this film is used, a new problem arises when chemicals leak from this part. The purpose of the present invention is to avoid excessively high pressure filter cloth Summary of the invention: In order to solve the above problem, the present invention improves the sodium-based dechlorinating agent. More specifically, the sodium-based dechlorinating agent of the present invention contains sodium bicarbonate and a hydrophilic anti-caking agent. Mixtures with a static angle of 40 ° or higher, a dispersion of less than 50, and a floodability index of less than 9'0. Pulses of air-to-bag hydrogen chloride printed by the Consumer Cooperative of the Intellectual Property Bureau of the Ministry of Economic Affairs The reaction is generated in the filter cloth, and the Leakage of leftovers. Chlorine and double woven glass cloth that neutralize the residual film are damaged or peeled off, face down or attach to the dust collector (please read the precautions on the back before filling this page). Sodium-based dechlorinating agent, in which the hydrophilic anti-caking agent has slight adhesion, and the flowability of sodium bicarbonate and anti-caking agent particles becomes relatively slow: sodium bicarbonate or anti-caking agent particles will not enter Into the filter cloth, and a stable filter layer is formed on the surface of the filter cloth. As a result, it is possible to prevent excessive pressure drop or filter cloth leakage in the filter cloth. Use PT-D powder test made by Hosokawa Micron company Machine, measuring physical properties. This paper size is applicable to China National Standard (CNS) A4 (210 X 297 mm) -6- 472125 A7 B7 V. Description of the invention (4) (Please read the precautions on the back before filling this page The measurement of the static angle is carried out by passing the powder sample through a screen with a diameter of 8 mm and a mesh opening of 7 10 / zm under the screen vibration, and slowly passing the sieved sample from a height of 160 mm Funnel drops to 80 mm diameter When the angle between the production line of the cone formed by the powder and the horizontal plane is generated, take a smaller value based on the higher flowability. Measure the amount of powder falling until the angle of rest is generally stable. The flowability index 値 is a judgment criterion for digitally evaluating the flooding characteristics. By determining the flowability index 测量, the drop angle, the difference angle, and the dispersibility measured from Tables 5 and 6, the flowability index 値 is defined In order to aggregate the Tannian indices: a larger 値 corresponds to a higher flowability characteristic. Now the definition of individual physical properties will be explained. The liquidity index is determined by an index determined in a similar manner. From the measurement angle of rest angle, compressibility, spatula angle, and coefficient of consistency, and expressed as the sum of these indices. The angle of rest is determined in the manner described above. The compressibility is defined as: (the overall density of the filling-the overall density of ventilation) / the total density of the filling X 1 ◦ ◦ The overall density of ventilation printed by the employee consumer cooperative of the Intellectual Property Bureau of the Ministry of Economic Affairs is determined by shaking the screen The powdery sample is passed through a sieve with a diameter of 8 mm and a mesh opening of 7 1 0, and the powder under the sieve is packed in a container with an internal volume of 100 m3 as the measured powder mass. . The method of determining the overall density of the filling is to pat the container containing the powder, and take a shot at 180 times' over a time period of 180 seconds and measure the mass corresponding to a volume of χ 〇 〇 c m 3. The size of the paper is applicable to the Chinese National Standard (CNS) A4 specification (210 X 297). 472125 Printed by the Consumer Cooperative of the Intellectual Property Bureau of the Ministry of Economic Affairs A7 B7 V. Description of the invention (5) The method of determining the knife angle is to use metal A prepared spatula with a size of 120 × 2 2 mm was kept horizontal and the inclination angle of the powder side surface accumulated on it was measured. Consistency is defined as the cumulative mass distribution obtained from the particle size distribution measured by sieve analysis, divided by 60% of the cumulative undersize distribution divided by the cumulative smaller size distribution1値 with a particle size at 0%. The particle size distribution can be determined by different methods, such as sieve analysis and laser diffraction scattering methods, which can reflect the particle size of the powder to be measured and the like. The 値 ′ measured by the laser diffraction scattering method of the present invention is measured using a “Microtrack F R A 9 2 2 0” manufactured by Nikkiso Co., Ltd. The method of determining the drop angle is to apply a fixed impact force to the powder cone formed for the purpose of measuring the angle of rest with a vibrator attached to the measuring instrument, and measure the tilt of the cone formed by the fall. angle. The difference angle is determined by subtracting 値 from the drop angle from 静止 at the static angle. The dispersibility is determined by throwing a 10 g powder sample at a time from 6 1 •........ Cm to a 10 cm diameter glass surface with a concave surface facing downward. The powder sample is scattered on The mass outside the glass is a percentage relative to the total mass of the powder sample that was dropped. Powder samples higher than this are usually highly dispersible and flowable. The sodium bicarbonate should preferably have an average particle size in the range from 2 // m to 3 0 // m. When the average particle diameter is larger than 30 #m, the reaction between the sodium-based dechlorinating agent and hydrogen chloride becomes insufficient; on the other hand, when the average particle diameter is smaller than 2 # m, it takes a lot of time and labor. In order to make the sodium-based dechlorinating agent, the paper size applies the Chinese National Standard (CNS) A4 specification (210 X 297 mm) —M -------- Order -------- line (please read first Note on the back page, please fill in this page again) -8- 472125 A7 B7 V. Description of the invention (6) A sufficient response has been achieved. The average particle size can meet the demand within the range of 2 # m to 3 0 # m. 2 // m to 1 0 #m can have a higher response (please read the precautions on the back before filling this page), so it is more recommended. Available anticaking agents typically include silicone, magnesium stearate, calcium stearate, and magnesium carbonate. The hydrophilic anti-caking agent in the present invention should preferably contain silicone, and more preferably should be mixed in the total mass of the dechlorinating agent in an amount of 0.1% or more. An amount of less than 0.1% is not sufficient to obtain an anti-caking effect. Because the hydrophilic anti-caking agent does not dissolve in water, it takes a considerable amount of time and labor to dispose of the dechlorination residue. Therefore, the hydrophilic anti-caking agent should preferably be 0.1% to An amount in the range of 5% is mixed in the total mass of the dechlorinating agent. Furthermore, the average particle size of the hydrophilic anti-caking agent should preferably be in the range of 0.0 0 1 # m to 1 # m. A smaller average particle size will have a more prominent anti-caking effect, but it is not technically easy to make the particle size of the powder less than 0. 0 0 1 # m in a low-cost 'industrialized manner; the average particle size is greater than 1 m There will be less anti-caking effect. So it should be in the range of ◦. 0 ◦ 1 # m to 1 // m. Printed by the Consumer Cooperative of the Intellectual Property Bureau of the Ministry of Economic Affairs, the waste treatment equipment in the present invention includes a thermal cracking reactor, which thermally cracks waste to generate thermal cracking gas and thermal cracking residues mainly containing non-volatile components; a separation mechanism The pyrolysis residue is divided into flammable and non-combustible components; the combustion melting furnace can allow the pyrolysis gas and flammable components to be introduced for combustion, and the melting furnace stone and flue gas are discharged; the first flue gas processing mechanism is removed Dust in flue gas; the second flue gas processing agency applies the Chinese National Standard (CNS) A4 (210 X 297 mm) at this paper scale -9-Α7 Β7 V. Description of the invention (7) Since the first smoke The flue gas discharged from the flue gas treatment mechanism is dechlorinated by adding a dechlorinating agent; the separator adds water to the dechlorination residue generated by the second flue gas treatment mechanism, and The water-insoluble composition that is insoluble in water is separated from the aqueous solution of the dechlorination residue; the p Η modifier adjusts the ρ Η of the aqueous solution remaining after the water-insoluble composition is separated by the separator; and at least another Dioxin removal unit to remove dioxin residues from the second flue gas treatment mechanism and / or dioxin and the like from aqueous solutions whose ρ Η has been adjusted with ρ Η modifier; sodium The dechlorinating agent is added to the second flue gas treatment mechanism. As described above, the dioxin removal unit that removes dioxin and the like from the aqueous solution in which ρ Η has been adjusted by the ρ Η modifier can be provided as the dioxin removal unit. A dioxin removal unit capable of removing dioxin and similar dioxins in the dechlorination residue generated by the second flue gas treatment mechanism can be provided instead of the dioxin removal unit for dioxin removal of the adjusted aqueous solution ρ Η. When a dioxin and similar dioxin removal unit is provided to remove the dechlorination residue generated by the second flue gas treatment mechanism, the dioxin removal unit can almost completely remove dioxin and the like, but it is not removed for removal. Dioxin and the like, the second dioxin removal unit may be provided downstream of the P (R) modifier. By using a chelating resin or a chelating agent (hereinafter collectively referred to as "chelating substance J"), it is possible to remove the TTTT left in the aqueous solution after separating the water-insoluble composition. Water ° Furthermore, it can be treated in the above waste The upstream of the second flue gas treatment mechanism in the equipment is mixed with sodium bicarbonate and hydrophilic anti-caking agent. The paper size is applicable to China National Standard (CNS) A4 (210 X 297 mm) (Please read the note on the back first) Please fill in this page for further information.) Packing — Order II ------- I-line Consumer Consumption Cooperation of Intellectual Property Bureau of the Ministry of Economics Du printed-10- Printed by the Employee Consumption Cooperative of Intellectual Property Bureau of Ministry of Economic Affairs 472125 Α7 _____ Β7 V. Invention The mixer of (8) and the honing machine for honing sodium bicarbonate. The p Η modifier can be added downstream of the p Η modifier in the waste treatment equipment described above, which has been adjusted by the p 改性 modifier. Mercury in aqueous solution. The method in the flue gas dechlorination method of the present invention comprises the steps of adding the above-mentioned sodium-based dechlorinating agent to the flue gas, so that the hydrogen chloride contained in the flue gas and the sodium-based dechlorinating agent Reaction to remove it. Furthermore, this The method for dechlorination of flue gas in the Ming Dynasty includes the following steps: reacting hydrogen chloride contained in the flue gas with a sodium-based dechlorinating agent to remove the residue of dechlorination; removing dioxin and the like from the dechlorination residue; Then, water is added to dissolve the dechlorination residue, and a water-insoluble composition that cannot be dissolved in water is separated from the aqueous solution in which the dechlorination residue is dissolved; and P 对 is adjusted for the aqueous solution remaining after the water-insoluble composition is separated. In the gas dechlorination method, dioxin and the like that cannot be completely removed can be removed again after the adjustment of ρ 。. Brief description of the figure: Figure 1 is a schematic diagram of the system, illustrating that the sodium-based dechlorinating agent method of the present invention can be used for dechlorination. An example of a chlorine device. Figure 2 is a schematic diagram of the system, illustrating another example of a dechlorination device that can be performed with the sodium-based dechlorinating agent method of the present invention. Figure 3 is a schematic diagram of the system, still illustrating the sodium-based dechlorinating agent of the present invention Method, another example of a dechlorination device can be performed. FIG. 4 is a schematic diagram of the system, illustrating another example of a dechlorination device that can be performed with the sodium-based dechlorinating agent method of the present invention. The dimensions are applicable to China National Standard (CNS) A4 (210 X 297 mm) I ^ -------- Order --------- Line- (Please read the precautions on the back before filling in this Page) -11-472125 A7 B7 V. Description of the invention (9) Figure 5 is not intended to illustrate the system. 'Describes another example of the dechlorination device that can be performed with the sodium-based dechlorinating agent method of the present invention. Figure 6 is a schematic diagram of the system' A waste treatment equipment is described as another example of the present invention. Comparison of main components 2 Thermal cracking reactor 4 Separator 5 Honer 6 Combustion melting furnace 8 Heat exchanger 10 Waste heat boiler 12 Cooling tower 14 First episode Dust collector 16 Second dust collector 18 Honer 2 0 Flue 2 2 Dissolution tank 2 4 Relay tank 2 6 Separator 2 8 p pAdjustment tank 32 Dioxin removal unit 32a Dioxin removal unit 3 4 Wastewater tank (please read first Note on the back then fill out this page) !! _ —Order --------- Printed by the Consumers' Cooperative of the Intellectual Property Bureau of the Ministry of Economic Affairs. The paper size is applicable to China National Standard (CNS) A4 (210 X 297 mm) -12- 472125 A7 B7 V. Description of the invention (ίο) Printed by the Consumer Cooperative of the Intellectual Property Bureau of the Ministry of Economic Affairs 3 5 Mixer a Waste b Thermal cracking residue c Thermal cracking carbon d 1 Valuable articles d 2 Residue e Melting furnace stone f 1 Dust f 2 Dust f 3 dust g dechlorination if g 1 sodium bicarbonate g 2 hydrophilic anti-caking agent A hot air G 1 pyrolysis gas G 2 combustion flue gas G 3 flue gas G 4 flue gas G 5 flue gas G 6 Flue gas G 7 Flue gas h Dechlorination residues i Water j Aqueous solution (please read the precautions on the back before filling this page) Loading -------- Order --------- The paper size of the paper is applicable to the Chinese National Standard (CNS) A4 (210 X 297 mm) -13- 472125 Printed by the Consumer Cooperative of the Intellectual Property Bureau of the Ministry of Economic Affairs A7 B7 V. Description of the invention (11) k Water-insoluble composition w Water Detailed description of preferred specific examples: Specific examples of the present invention will be described with reference to the drawings. Fig. 1 is a schematic diagram of a system capable of performing a dechlorination device by the sodium-based dechlorinating agent method used in the present invention. This example represents the application of the present invention to the flue gas dechlorination of, for example, the flue gas G5 produced on the flue. As shown in FIG. 1, the flue thermal dechlorination device includes a first dust collector 1 4 ′ as a first flue gas processing mechanism and a second dust collector 16 as a second flue gas processing mechanism to perform Two-stage dust collection. The flue gas G 5 is produced when the processed waste is sent to the first dust collector 14 & 'the first dust collector 1 4 removes the dust from the flue gas G 5 (incineration fly ash) ί 1' The flue gas G 6 from which the dust f 1 has been removed is sent to the second collector 16 ′. At this time, the sodium-based dechlorinating agent g of the present invention is added to the flow channel in the upstream of the second dust collector 16. Because the dust f 丨 has been removed in the first dust collector 14 in advance, the dechlorination residue h in the second dust collector 16 is almost free of dust f 1. As a result, compared with the case of a single dust collector 'This dechlorination residue h is easier to dispose of. The sodium-based dechlorinating agent g contains a mixture of sodium bicarbonate (sodium bicarbonate: Na H C 0 3) and a hydrophilic anti-caking agent. Sodium bicarbonate should be honed to an average particle size in the range of 2 // m to 3 〇 # m, or preferably 2 # m to 1 0 // m ′ and in an amount of 0.1% by mass or more Mixed with silicone-based hydrophilic anti-caking agent, or preferably in the range of 0.1 mass% to 5 mass%. This paper size is applicable to China National Standard (CNS) _A4 specifications (210 X 297). (Please read first Note on the back, please fill in this page again.) Assemble !! Order --------Line -14- 472125 Consumer Co-operation of Intellectual Property Bureau of the Ministry of Economic Affairs Du printed A7 B7 5. Inventory (12). The average particle diameter of the hydrophilic anti-caking agent should be in the range of Q. 0 0 1 // m to 1 / zm, or preferably in the range of 0. 00 1 // m to 0.1 μm. Available hydrophilic anti-caking agents include, for example, fumed hydrophilic silicone manufactured by Tokuyama Corporation. When the sodium bicarbonate particles are honed to a particle size ranging from 2 # m to 3 0 # m, the reaction goes from the particle surface to the inside, and the small particle size ensures good adhesion to the filter cloth and satisfactory utilization efficiency. When the flue gas contains sulfur oxides, the sodium-based dechlorinating agent g can be used as a desulfurizing agent, making it possible to complete desulfurization in the second dust collector 16 while dechlorinating. When sodium-based dechlorinating agent g is added, sodium chloride (Na C 1) produced by reaction with hydrogen chloride (HC 1) contained in the flue gas is discharged from the second dust collector 16 as a dechlorination residue. The dechlorinated flue gas G 7 is emitted from the flue 20 as a purified gas. On the other hand, the dechlorination residue h removed by the second dust collector 16 is added with water i and dissolved in the dissolution tank 22, and further sent to the relay tank 24, and stored as an aqueous solution j. When water i is added, the water-soluble composition in the dechlorination residue h is dissolved in water, but the water-insoluble composition k is insoluble in water and becomes a suspended substance in the aqueous solution. Then, the produced aqueous solution j is sent to a separator 26, which is separated by, for example, filtration, and the water-insoluble composition k which forms a suspension is separated from the aqueous solution. The separated water-insoluble composition k is returned to a thermal cracking reactor (not shown) as described later, and finally melted in a combustion furnace. After being converted into a molten furnace stone, it is discharged outside the system. At this time, dioxin and the like in the water-insoluble composition k can be decomposed and completely removed in a combustion melting furnace. This paper size applies to China National Standard (CNS) A4 (210 X 297 mm) 』-15--------- ^ --------- ^ (Please read the notes on the back first (Fill in this page again) 472125 Printed by the Consumer Cooperatives of the Intellectual Property Bureau of the Ministry of Economic Affairs A7 B7 V. Description of the invention (13) The remaining water solution 1 after separating the water-insoluble composition k contains water-soluble composition 'Send it to the next adjustment P Η Ρ Η is adjusted in the program of the slot 2 8. A pH adjusting agent such as hydrogen chloride (H C 1) acidic substance is added to neutralize the unreacted dechlorinating agent dissolved in water. Furthermore, dioxin and the like sent to the dioxin removal unit can be removed. In order to remove dioxin and the like ', an aqueous solution is passed through a packed bed of activated carbon or the like, and an activated carbon adsorption method for removing dioxin and the like is used. The aqueous solution 1 obtained by removing dioxin from the remaining aqueous solution 1 described above is stored in a wastewater tank 34 as treated water w. Among the above water-soluble compositions, only aqueous solutions containing soluble sodium salts such as sodium chloride are adjusted to ρ Η before being discharged to the ocean, rivers and sewage disposal sites. As for the minor content of dioxin, dioxin and the like in the aqueous solution 1 are removed only after separation of the water-insoluble composition. This method is simpler and less expensive than a thermal cracking device. As shown in FIG. 1, in order to remove dioxin and the like contained in the aqueous solution 1 remaining from the separator 2 6, a dioxin removal unit 3 2 is provided downstream of the ρ Η adjustment tank 2 8. Diol and similar in chlorine residue h. More specifically, as shown in FIG. 2, the dioxin removal unit 3 2 a is arranged between the second dust collector 16 and the dissolution tank 22, so that the dechlorination residue h from the second dust collector 16 Dioxin and the like contained in the dechlorination residue h are removed before being dissolved in water. A dioxin removal unit 32a which can be used includes, for example, a thermal dechlorination unit. The characteristic 'Dioxin and the like described above can be almost completely removed from the dechlorination residue discharged from the dioxin removal unit 32a. Therefore, not only the water-insoluble composition k, but also the remaining aqueous solution 1, almost the size of this paper applies Chinese National Standard (CNS) A4 specifications (210 X 297) (please read the precautions on the back before filling in this Page) " -------- Order --------- line | -16- 472125 A7 B7 V. Description of the invention (14) Contains dioxin or the like. (Please read the precautions on the back before filling in this page.) Furthermore, the characteristics shown in Figure 3 can also be used, in which the dioxin removal unit 3 2 is arranged downstream of the P Η adjusting groove 28 and the dioxin removal The unit 3 2 a is arranged between the second dust collector 16 and the dissolving tank 2 2. That is, dioxin and the like can be almost completely removed by the dioxin removal unit 3 2 a. If there is a problem that dioxin and the like remain after removal, the dioxin removal unit 32 can still completely remove dioxin and the like after the adjustment of PP. Printed by the Consumer Cooperative of the Intellectual Property Bureau of the Ministry of Economic Affairs can also adopt the characteristics shown in Figure 4, where the setting mechanism of the mixer 35 and the honing machine 18 is honing sodium bicarbonate and mixed hydrophilic anti-caking agent. Generally, because sodium bicarbonate g 1 has an average particle size in the range of 50 / zm to 2 7 0 // m, the steps included in the program include: 0.1% by mass of sodium bicarbonate g 1 Amount, add a hydrophilic silicone with an average particle size in the range of ◦. 0 0 1 // m to 1 Μ IB, as a hydrophilic anti-caking agent g 2; in a mixer 3 5 mix sodium bicarbonate g 1 and Hydrophilic anti-caking agent g 2; honing the resulting mixture in a honing machine 18 so that the average particle size is in the range of 2 μm to 3 0 // m to produce a sodium-based dechlorinating agent g. This sodium-based dechlorinating agent g is added to the flue gas G6, and the powder 麈 f1 thereof has been removed by the first dust collector 14. Because the size of sodium bicarbonate honing to an average particle size in the range of 2 # m to 3 0 # m is small, it will react from the particle surface to the inside, and has good adhesion properties to the filter cloth of the bag dust collector . Therefore, satisfactory utilization efficiency can be ensured. As shown in Figure 4, the Dioxin removal unit 3 2 is arranged downstream of the pH adjustment tank 28, and the Dioxin removal unit 3 2 a can also apply the Chinese National Standard (CNS) A4 specification to this paper size ( 210 X 297 mm) -17- 472125 A7 B7 printed by the Consumer Cooperatives of the Intellectual Property Bureau of the Ministry of Economic Affairs 5. Description of the invention (15) The characteristics shown in Figure 2 are arranged in the second dust collector 16 and the dissolution tank 2 Between 2. Furthermore, as shown in FIG. 3, the dioxin removal unit 3 2 may be disposed downstream of the P Η adjustment tank 28, and the dioxin removal unit 3 2 may be disposed at the second dust collector 16 and the dissolution tank 2. Between 2. As shown in FIG. 5, it is also possible to arrange a mercury removal unit 30 between the pH adjustment tank 28 and the dioxin removal unit 32, with the purpose of removing the water remaining from the separator 26, which is contained in the valley liquid 1. Dear. By using this characteristic, p of the aqueous solution 1 remaining after the water-insoluble composition k is separated by the separator 2 6 is adjusted in the p Η adjustment tank 2 8, and mercury belonging to a heavy metal can be removed by the mercury removal unit 30. Remove. Mercury can be removed, for example, by precipitation, ion exchange or adsorption. In the Shendian method, possible techniques include precipitation that produces a mercury sulfide form, or the use of heavy metal scavengers with dithiocarbamates and the like. In the ion exchange method, when mercury is present as an anion such as a halogenated complex ion, an anion exchange resin is used. In the adsorption method, a chelating resin, activated carbon, or activated coke having a high selectivity for a specific heavy metal is utilized by a chelating effect. Useful chelating resins include, for example, polypropylene, polystyrene, or phenol resins as the matrix, and types such as thiol, dithiocarbamate, isothuronium, diphenylthiosulfone, thiourea, or polyamine as the coordination free base. Useful activated carbon types include, for example, gas activated carbon, zinc chloride activated carbon, granular activated carbon, coconut shell activated carbon, and granular activated carbon black. Among these methods, a method using a chelating substance such as a chelating agent or a chelating resin is preferable because it is simple and accurate. The mercury-removed aqueous solution is introduced into the dioxin removal unit 3 2 and the Chinese national standard (CNS) is applied at this paper scale. A4 size (210 X 297 mm) (Please read the precautions on the back before filling this page) I installed! Order--I--! 1 · Line · -18- 472125 Printed by the Consumer Cooperatives of the Intellectual Property Bureau of the Ministry of Economic Affairs A7 B7 V. Description of Invention (16) Remove dioxin and the like. The applicable dioxin removal method is the same as the one shown in Fig. 1 above. In FIG. 5, the 'dioxin removal unit 32 is disposed downstream of the pΗ adjustment tank 28 located downstream of the mercury removal unit 30. However, as shown in FIG. 2, the dioxin removal unit 3 2 a may be disposed between the second dust collector 16 and the dissolution tank 22. Furthermore, as shown in FIG. 3, the dioxin removal unit 32 is disposed downstream of the pΗ adjustment tank 28, and the dioxin removal unit 3 2a may be disposed between the second dust collector 16 and the dissolution tank 22 between. A waste treatment apparatus for treating waste and the generated flue gas will now be described with reference to FIG. Fig. 6 is a schematic diagram of a system illustrating an example of a waste disposal apparatus according to the present invention. As shown in FIG. 6, in this waste treatment equipment, the waste a of municipal waste is honed below 150 mm 2, and then introduced into the thermal cracking reactor 2 by an introduction mechanism such as a screw feeder. . For example, a horizontal rotary drum is used as the thermal cracking reactor 2. The interior of the thermal cracking reactor 2 is maintained in a low-oxygen environment by a sealing mechanism (not shown), and heat exchange is arranged downstream of the combustion melting furnace 6. The hot air A in the downstream heated by the heater 8 is introduced from the line L 1. The waste a leading to the thermal cracking reactor 2 is heated with hot air A to a temperature in the range of 30 ° to 600 ° C, or usually about 4500 ° C, so that the waste a is thermally cracked. A thermal cracking gas G1 and a non-volatile thermal cracking residue b are generated. The thermal cracking gas G 1 and thermal cracking residue b generated in the thermal cracking reactor 2 are separated by a discharge unit (not shown). The thermal cracking gas G 1 is transported via a line L 2, which is a thermal cracking gas. The paper size of this paper applies to China National Standard (CNS) A4 (210 X 297 mm) I! ----- · " 1--Order ------- line (please read the precautions on the back first) (Fill in this page again) -19- 472125 A7 B7 printed by the Consumer Cooperatives of the Intellectual Property Bureau of the Ministry of Economic Affairs 5. Description of the invention (17) The pipeline to the burner of the combustion furnace 6. According to the findings obtained by the present inventors, the thermal cracking residue b, which changes with the type of waste a, can be found to contain the following mass%: most of the flammable components relatively contain fine particles: 10 to 6 0% relatively fine ash: 5 to 40% coarse metal granules: 7 to 50% coarse residue, ceramics, cement, etc .: 10 to 60% at a relatively high temperature of about 4 5 0 t The discharged thermal cracking residue b is cooled to about 80 ° C. in a cooling unit (not shown in the figure) and is introduced into the separator 4 as a separation mechanism, where the residue is divided into pyrolytic carbon of a combustible composition c, and non-combustible valuable plutonium article d 1 and residue d 2. Vibrating screens, magnetic separators, and aluminum separators can be used as the separator 4 as well as known separators. The thermally cracked carbon c and the residue d 2 separated from the non-combustible components and then discharged are honed by a rolling type, a tube type, a rod type, or a ball type type honing machine 5 and then sent to a combustion melting furnace 6. The honing machine 5 is appropriately selected according to the type and characteristics of the waste. In the honing machine, the pyrolyzed carbon c and the residue d 2 should preferably be honed to a particle size of 1 mm or less, and then sent to the burner of the combustion melting furnace 6 through the line L 3. On the other hand, the combustion air, thermally decomposed gas G1, and thermally cracked carbon c delivered by a fan (not shown) are burned in a combustion melting furnace at a temperature in a high temperature range of about 130 ° C. After this combustion, the burning ash produced by the relatively fine ash particles of pyrolysis of carbon c and residue d 2 will melt. This paper is sized to the Chinese National Standard (CNS) A4 (210 X 297 mm) 1 ---- ------ Ί! Β --------- ^ I (Please read the notes on the back before filling this page) -20- 472125 A7 B7 V. Description of the invention (18) (Please read first Note on the back? Matters need to be filled out on this page again) to produce melting furnace stone e. The hearth stone is thrown into the water tank (not shown) from the bottom outlet of the hearth of the combustion melting furnace 6, and the melting hearth e is converted into a water-based granulated hearth. An apparatus (not shown) is used to restrict the water-granulated hearthstone to a specified shape, or to make it into reusable building materials or paving materials. The combustion flue gas G 2 generated in the combustion melting furnace 6 of the waste treatment facility is heat-recovered in the heat exchanger 8 to become the flue gas G 3, which is introduced into the waste heat boiler 10 which can recover heat, The flue gas G 3 is transformed into a flue gas G 4. The flue gas G 4 is sent to a cooling tower 12 to reduce its temperature. The flue gas G 5 that has been cooled in the cooling tower 12 is sent to the first dust collector 1 4. The dust f 2, f 3 and f 1 are collected in the waste heat boiler 10, the cooling tower 12 and the first dust collector 14 respectively. With the pyrolysis carbon c separated in the separator 4, the gas passes through the line L 3 And L 4 is returned to the burner of the combustion melting furnace 6, and is burned and melted in the combustion melting furnace 6 to become a furnace stone. The consumer cooperative of the Intellectual Property Bureau of the Ministry of Economic Affairs printed the water-insoluble composition k separated by the separator 2 6 and returned to the thermal cracking reactor 2 via the line L 5, and finally burned and melted in the combustion melting furnace 6 to become a furnace stone. In this procedure, heavy metals are rendered harmless by forming hearthstone. The subsequent processing of the flue gas G 5 sent to the first dust collector 14 is the same as that shown in Fig. 5, so its explanation is omitted here. The subsequent processing of the flue gas G 5 sent to the first dust collector 14 can be performed using a processing system having the characteristics shown in Figs. Examples The sodium-based dechlorinating agent of the present invention was used for practical experiments. Hydrophilicity This paper is sized for China National Standard (CNS) A4 (210 X 297 mm) -21-472125 A7
經濟部智慧財產局員工消費合作社印製 五、發明說明(19) 防結塊劑與本發明的鈉系脫氯劑混合(以下簡稱爲「鈉系 脫氯劑A」),爲了比較的目的,另外製備以鈉系脫氯劑 與取代親水性防結塊劑的疏水性防結塊劑混合(以下簡稱 爲「鈉系脫氯劑B」),並亦進行其實際應用的實驗。鈉 系脫氯劑A含有平均粒徑爲8 # m的碳酸氫鈉,及混合著 作爲防結塊劑、平均粒徑爲〇 . 〇 1 3 # m的親水性蒸燻 (fumed )矽膠,其量爲1質量%。鈉系脫氯劑b含有平均 粒徑爲8 // m的碳酸氫鈉,及混合著作爲防結塊劑、平均 粒徑爲〇 · 〇 1 3 // m的疏水性蒸燻矽膠,其量爲1質量 %。對於防結塊劑加到鈉系脫氯劑A及B的不同數據如表 1所示,在表1中,防結塊劑A及防結塊劑b分別代表加 到鈉系脫氯劑A及鈉系脫氯劑B中的防結塊劑。 ^--------訂---------線 (請先閱讀背面之注意事項再填寫本頁) 表1 防結塊劑A 防結塊劑B 種類 親水性 疏水性 名稱 fumed Ϊ夕膠 fumed砂膠 製造商 TOKUYAMA 公司 TOKUYAMA 公司 產品名稱 REOLOSIL QS-102 REOLOSIL MT-10 添加量 1質量% 1質量% 粒徑 0.014 μιη 0.013 μ m 化學組成 矽膠(Si〇2) 矽膠(Si〇2) $紙張尺度適用中國國家標準(CNS)A4規格(210 X 297公釐) -22- 472125 A7 __B7 _____ 五、發明說明(2〇) (請先閱讀背面之注意事項再填寫本頁) 以上述已添加防結塊劑的鈉系脫氯劑A及B,決定其 靜止角度、可流動性指數及分散性。利用Hosokawa Micron 公司所製造的粉末測試機P T - D,以上述的測量方法進 行分析。在本實例中的鈉系脫氯劑A靜止角度的測量値爲 5 3 °,分散性爲2 1 %,且由表5及6讀到靜止角度指數 爲1 2而分散性爲1 6。同樣的,其他項目的測量得到可 氾流性指數値爲7 4,結果建議爲具有高度的可氾流性。 對鈉系脫氯劑B亦進行相同的評估,顯示可氾流性指數値 爲9 0 ,結果建議爲具有很高度的可氾流性。結果如表2 所示。 表2 鈉系脫氯劑A 鈉系脫氯劑B 測量値 指數 測量値 指數 靜止角度Γ ) 53 12 38 18 可分散性(%) 21 16 57 25 可氾流性指數 — 74 — 90 經濟部智慧財產局員工消費合作社印製 比較鈉系脫氯劑A及鈉系脫氯劑B獲得如下的發現, 就粉末的特性而言,鈉系脫氯劑A表現出類似於氫氧化耗 的一般可流動性,且容易與水混合;鈉系脫氯劑B表現出 很高的可流動性,會排斥水而無法適應水。 爲了獲知實際的應用性,在實廠中進行袋式集塵器可 本紙張尺度適用中國國家標準(CNS)A4規格(210 X 297公釐) -23- 472125 經濟部智慧財產局員工消費合作社印製 A7 B7 五、發明說明(21) 操作性的實驗,結果如表3所示。鈉系脫氯劑A及B皆使 用含有鐵弗龍鋪層的雙織玻璃布的濾布,因爲一部分的濾 布上可觀察到鐵弗龍鋪層的剝落,鈉系脫氯劑B的藥劑洩 漏量較大。 表3 鈉系脫氯劑A 鈉系脫氯劑B 濾布種類 鐵氟離鋪層 鐵氟離鋪層 濾布壓降 Μ.9χ l〇2Pa 之2xl03Pa或更多 藥劑洩漏 <lmg/Nm3或更少 <120mg/Nm3或更少 就鈉系脫氯劑A而言,瀘布的壓降很低,最高達 4 · 9xl〇2Pa ,自濾布的洩漏最高達img/Nm3 ,所以不會造成實際的問題。相反地,就鈉系脫氯劑B而 言,濾布的壓降很高,達2 x 1 0 3 P a ,自濾布亦有高浅 漏重爲1 2 Omg/Nm3 ’所以顯不貫際應用有困難。 單獨使用雙織玻璃布作爲濾布及使用在表面上具有鐵 氟龍鋪層的雙織玻璃布作爲濾布,進行洩漏濃度與壓降的 實驗,結果如表4所示。 本紙張尺度適用中國國家標準(CNS)A4規格(21〇 X 297公釐) ^ Μ--------^—-------^ (請先閱讀背面之注意事項再填寫本頁) -24- A7 '^^ --------B7 五、發明說明(22 ) —_ 袠4 ----_ 鈉系脫氯劑A 鈉系脫氯劑Β 雙織玻璃布 洩漏濃度 (mg /Nm3) ___壓降(Pa) 0 4, 102 1 5000 8.5χ102 雙織玻璃布+鐵氟龍 鋪層 洩漏濃度 0 0 (mg /Nm3) 壓降(Pa) 1.8χ 102 7.5χ102 (請先閱讀背面之注意事項再填寫本頁) 經濟部智慧財產局員工消費合作社印製 在單獨使用雙織玻璃布的情況中,對鈉系脫氯劑B而 言,洩漏濃度與壓降二者都很大;但對鈉·系脫氯劑A而言 ,洩漏濃度與壓降二者都很小。在使用表面上具有鐵氟龍 鋪層的雙織玻璃布的情況中,對鈉系脫氯劑A及B二者而 言,皆無洩漏濃度,但鈉系脫氯劑B的壓降很大。 本紙張尺度適用中國國家標準(CNS)A4規格(21〇 x 297公釐) -25- 472125 A7 B7 五、發明說明(23) #1餚, $ (I) c〇Printed by the Consumer Cooperative of the Intellectual Property Bureau of the Ministry of Economic Affairs. 5. Description of the invention (19) The anti-caking agent is mixed with the sodium-based dechlorinating agent of the present invention (hereinafter referred to as "sodium-based dechlorinating agent A"). For comparison purposes, In addition, a sodium-based dechlorinating agent is mixed with a hydrophobic anti-caking agent instead of a hydrophilic anti-caking agent (hereinafter referred to as "sodium-based dechlorinating agent B"), and its practical application experiment is also performed. Sodium-based dechlorinating agent A contains sodium bicarbonate having an average particle size of 8 # m, and a hydrophilic fumigant silicone gel having an average particle size of 0.03 as an anti-caking agent. The amount was 1% by mass. The sodium-based dechlorinating agent b contains sodium bicarbonate having an average particle diameter of 8 // m, and a hydrophobic fumigant silicone mixed with an average particle diameter of 0 · 〇1 3 // m as an anti-caking agent. It is 1% by mass. The different data for the anti-caking agent added to the sodium-based dechlorinating agent A and B are shown in Table 1. In Table 1, the anti-caking agent A and the anti-caking agent b respectively represent the addition to the sodium-based dechlorinating agent A. And anti-caking agent in sodium-based dechlorinating agent B. ^ -------- Order --------- Line (Please read the precautions on the back before filling this page) Table 1 Anti-caking agent A Anti-caking agent B Kind of hydrophilic and hydrophobic Name fumed Fumed sand glue manufacturer TOKUYAMA company TOKUYAMA company product name REOLOSIL QS-102 REOLOSIL MT-10 Addition amount 1% by mass 1% by mass Particle size 0.014 μm 0.013 μm Chemical composition Silicone (Si〇2) Silicone (Si 〇2) $ Paper size is applicable to China National Standard (CNS) A4 (210 X 297 mm) -22- 472125 A7 __B7 _____ V. Description of the invention (2〇) (Please read the precautions on the back before filling this page) Based on the sodium-based dechlorinating agents A and B to which the anti-caking agent has been added, the rest angle, flowability index and dispersibility are determined. The powder tester PT-D manufactured by Hosokawa Micron was used for analysis by the above-mentioned measurement method. The measurement of the rest angle of the sodium-based dechlorinating agent A in this example was 5 3 °, the dispersibility was 21%, and from Tables 5 and 6, it was read that the rest angle index was 12 and the dispersibility was 16. Similarly, the measurement of other items gives a floodability index 値 of 7 4 and the results suggest that it has a high floodability. The same evaluation was performed for the sodium-based dechlorinating agent B, which showed that the floodability index 値 was 90, and the result was suggested to have a high floodability. The results are shown in Table 2. Table 2 Sodium-based dechlorinating agent A Sodium-based dechlorinating agent B Measurement 値 Index measurement 値 Index rest angle Γ) 53 12 38 18 Dispersibility (%) 21 16 57 25 Flowability Index — 74 — 90 Ministry of Economy Wisdom Printed by the Consumer Cooperative of the Property Bureau, comparing sodium dechlorinating agent A and sodium dechlorinating agent B, the following findings were obtained. As far as the characteristics of the powder, sodium dechlorinating agent A shows a general flowability similar to the consumption of hydroxide It is easy to mix with water; sodium-based dechlorinating agent B shows high flowability, it will repel water and cannot adapt to water. In order to know the practical applicability, the bag dust collector used in the actual factory can be applied to the Chinese National Standard (CNS) A4 specification (210 X 297 mm) at this paper standard. -23- 472125 Printed by the Consumer Cooperative of the Intellectual Property Bureau of the Ministry of Economic Affairs System A7 B7 V. Description of the invention (21) Operational experiment, the results are shown in Table 3. Both sodium-based dechlorinating agents A and B use Teflon-laminated double-woven glass cloth filter cloth, because the Teflon-laminated peeling can be observed on some of the filter cloths, and the sodium-based dechlorinating agent B is the agent The amount of leakage is large. Table 3 Sodium-based dechlorinating agent A Sodium-based dechlorinating agent B Type of filter cloth Iron fluoride ion-laminated iron fluoride ion-laminated filter cloth pressure drop M. 9 × 10 2 Pa 2x103 Pa or more agent leakage < lmg / Nm3 Less < 120mg / Nm3 or less As far as the sodium-based dechlorinating agent A is concerned, the pressure drop of the cloth is very low, up to 4.9xl02Pa, and the leakage of the self-filtering cloth is up to img / Nm3, so it will not Cause practical problems. Conversely, with regard to sodium-based dechlorinating agent B, the pressure drop of the filter cloth is very high, reaching 2 x 1 0 3 P a, and the self-filter cloth also has a high and shallow leak weight of 1 2 Omg / Nm3 'so it is not consistent. Difficulties in international application. The leakage concentration and pressure drop experiments were performed using a double woven glass cloth alone as a filter cloth and a double woven glass cloth with a Teflon layer on the surface as a filter cloth. The results are shown in Table 4. This paper size is applicable to China National Standard (CNS) A4 (21〇X 297 mm) ^ Μ -------- ^ ----------- ^ (Please read the notes on the back before filling in (This page) -24- A7 '^^ -------- B7 V. Description of the invention (22) —_ 4 ----_ Sodium-based dechlorinating agent A Sodium-based dechlorinating agent B Double woven glass Cloth leakage concentration (mg / Nm3) ___ Pressure drop (Pa) 0 4, 102 1 5000 8.5χ102 Leak concentration of double woven glass cloth + Teflon laminate 0 0 (mg / Nm3) Pressure drop (Pa) 1.8χ 102 7.5χ102 (Please read the notes on the back before filling out this page) Printed by the Consumer Cooperative of the Intellectual Property Bureau of the Ministry of Economic Affairs When the double-woven glass cloth is used alone, the leakage concentration and pressure for sodium-based dechlorinating agent B Both drops are large; but for sodium-based dechlorinating agent A, both the leakage concentration and the pressure drop are small. In the case of using a double-woven glass cloth having a Teflon coating on the surface, there was no leakage concentration for both sodium-based dechlorinating agents A and B, but the pressure drop of sodium-based dechlorinating agent B was large. This paper size applies the Chinese National Standard (CNS) A4 specification (21〇 x 297mm) -25- 472125 A7 B7 V. Description of the invention (23) # 1 美食 , $ (I) c〇
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Q6-S §§ |卜 (3)¾ S寸 寸寸-CN寸 蟬涨胡 I 寸 刪·?iMIlg!69-09 (S 賴 _ ςς 寸lolz.寸 9寸 S9 寸9-卜5 95 06 S-A9 99 ¥扉 ^$,00 坩ΑΕΜ am 62寸 osco.s 61-0 (Blp起 (¾ o)·甦 本紙張尺度適用中國國家標準(CNS)A4規格(210 χ 297公釐) -26- 472125 A7 B7 五、發明說明(24 經濟部智慧財產局員工消費合作社印製 嗽尿#1痗®,f?s伥迄 9概 可分散性 指數 25 23 22.5 22 21 20 19.5 18 17.5 17 16 15 £ >50 49-44 43 42 41-36 35 34 33-29 28 27 26-21 20 差異角度 指數 25 24 22.5 22 21 20 • OO _· Ο» vn ' I C'''·' r—H i < >—< i 1 ί 1 >30 29-28 27 26 25 24 23 22-20 19 18 17-16 15 掉落角度 指數 25 24 22.5 22 21 20 19.5 18 17.5 17 16 15 10 11-19 20 21 22-24 25 26 27-29 30 31 32-39 40 流體性 指數 25 24 22.5 22 21 20 ^ OO IT^· <0^ T—H IT^· r—( r—i r—( i 1 i < (由上表推 衍的指數) >60 59-56 55 54 53-50 49 o oo ’ 寸 cn on 寸卜 寸寸 CO 寸寸 防止性措施 需要旋轉封 需要旋轉封 可氾流性 指數 80-100 60-79 可氾流性 很辰r(A) 高(B) 本紙張尺度適用中國國家標準(CNS)A4規格(210 X 297公釐) 裝--------訂---------綾 (請先閱讀背面之注意事項再填寫本頁) -27- 472125 A7 B7 五、發明說明(25) 如上所述,根據本發明因爲碳酸氫鈉鍛燒及與氯化氫 反應所導致的粒狀物、或防結塊劑的粒狀物不會卡在附於 集塵器的濾布中,因此可避免因碳酸氫鈉鍛燒及與氯化氫 反應所導致的粒狀物、或防結塊劑的粒狀物阻塞濾布。所 以可能可預防濾布中的壓降發生。 因爲碳酸氫鈉锻燒及與氯化氫反應所導致的粒狀物、 或防結塊劑的粒狀物不會卡在附於集塵器的濾布中,碳酸 氫鈉鍛燒及與氯化氫反應所導致的粒狀物、或防結塊劑的 粒狀物不會通過濾布而進入下游,因此可預防脫氯劑的拽 漏。 (請先閱讀背面之注意事項再填寫本頁) 經濟部智慧財產局員工消費合作社印製 本紙張尺度適用中國國家標準(CNS)A4規格(210 X 297公釐) -28-Q6-S §§ | Bu (3) ¾ S inch inch inch-CN inch cicada rose I inch delete? iMIlg! 69-09 (S Lai_ ς ς lolz. Inch 9 Inch S9 Inch 9-Bu 5 95 06 S-A9 99 ¥ 扉 ^ $, 00 Cruze ΑΕΜ am 62 Inch osco.s 61-0 (Blp from (¾ o) · The paper size of Suben is applicable to Chinese National Standard (CNS) A4 (210 χ 297 mm) -26- 472125 A7 B7 V. Description of the invention (24 Printed cough urine # 1 by the Consumer Cooperative of Intellectual Property Bureau of the Ministry of Economic Affairs ®, f? S 伥 9 to 9 dispersibility index 25 23 22.5 22 21 20 19.5 18 17.5 17 16 15 £ > 50 49-44 43 42 41-36 35 34 33-29 28 27 26-21 20 Angle of difference Index 25 24 22.5 22 21 20 • OO _ · Ο »vn 'I C' '' · 'r—H i < > — < i 1 ί 1 > 30 29-28 27 26 25 24 23 22- 20 19 18 17-16 15 Drop angle index 25 24 22.5 22 21 20 19.5 18 17.5 17 16 15 10 11-19 20 21 22-24 25 26 27-29 30 31 32-39 40 Fluidity index 25 24 22.5 22 21 20 ^ OO IT ^ · < 0 ^ T—H IT ^ · r— (r—ir— (i 1 i < (index derived from the above table) > 60 59-56 55 54 53-50 49 o oo 'inch cn on inch Bu inch inch CO inch inch preventive measures need rotary seals need rotary seals floodability index 80-100 60- 79 Flowability is very high r (A) High (B) This paper size is applicable to China National Standard (CNS) A4 (210 X 297 mm). Packing -------- Order ------ --- 绫 (Please read the notes on the back before filling this page) -27- 472125 A7 B7 V. Description of the invention (25) As mentioned above, according to the present invention, the sodium bicarbonate is calcined and reacted with hydrogen chloride. Granules or granules of the anti-caking agent will not get stuck in the filter cloth attached to the dust collector, so it can avoid granules caused by sodium bicarbonate calcination and reaction with hydrogen chloride, or anti-caking The granules of the blocking agent block the filter cloth. It may prevent the pressure drop in the filter cloth. The granules caused by the calcination of sodium bicarbonate and the reaction with hydrogen chloride, or the granules of the anti-caking agent will not It is stuck in the filter cloth attached to the dust collector, and the particulate matter caused by the sodium bicarbonate calcination and the reaction with hydrogen chloride or the anti-caking agent will not enter the downstream through the filter cloth. Leakage of chlorine agent. (Please read the precautions on the back before filling out this page) Printed by the Consumer Cooperatives of the Intellectual Property Bureau of the Ministry of Economic Affairs This paper applies the Chinese National Standard (CNS) A4 specification (210 X 297 mm) -28-
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CN111115999A (en) * | 2019-11-18 | 2020-05-08 | 绵阳油普能源科技有限责任公司 | Application and method of foaming agent in organic matter thermal decomposition to prevent coking and caking |
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EP1153645B1 (en) | 2004-01-21 |
DE60007843T2 (en) | 2004-12-30 |
US6482379B1 (en) | 2002-11-19 |
SG92759A1 (en) | 2002-11-19 |
SG115531A1 (en) | 2005-10-28 |
JP2001314757A (en) | 2001-11-13 |
US6949226B2 (en) | 2005-09-27 |
ES2214228T3 (en) | 2004-09-16 |
EP1153645A1 (en) | 2001-11-14 |
KR20010102818A (en) | 2001-11-16 |
JP3840632B2 (en) | 2006-11-01 |
KR100689949B1 (en) | 2007-03-08 |
DE60007843D1 (en) | 2004-02-26 |
US20020006372A1 (en) | 2002-01-17 |
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